APPENDIX H SAN DIEGUITO LAGOON W-19 INLET AND OCEAN ENTRANCE MAINTENANCE STUDY

APPENDIX H SAN DIEGUITO LAGOON W-19 INLET AND OCEAN ENTRANCE MAINTENANCE STUDY San Dieguito Lagoon W-19 Restoration Project Final EIR November 2018 Appendices

3780 Kilroy Airport Way, Suite 600 Long Beach, CA 90806 (562) 426-9551 Fax (562) 424-7489 www.moffattnichol.com MEMORANDUM To: From: Dokken Engineering Chris Webb and Weixia Jin Date: Subject: Revised Final San Dieguito Lagoon W-19 Inlet and Ocean Entrance Maintenance Study M&N Job No.: 7366-01 1. INTRODUCTION The San Dieguito Lagoon W-19 Restoration Project would restore additional habitats that historically occurred within the lagoon, taking into consideration constraints now imposed by existing adjacent land uses and other recently implemented and planned projects. The proposed project would encompass approximately 141 acres, including an area historically identified as a restoration opportunity by the JPA in their 2000 Park Master Plan for the Coastal Area of the San Dieguito River Valley Regional Open Space Park (Park Master Plan). ln addition, California Department of Transportation (Caltrans) and SANDAG identify the site as part of the overall wetland mitigation strategy for infrastructure projects along the North Coast Corridor within northern San Diego County in their 2013 Draft Final Public Works Plan and Transportation and Resource Enhancement Program (PWP/TREP). The proposed project is intended to be used for mitigation purposes for infrastructure projects being planned by SANDAG, Caltrans, and/or the City of San Diego (e.g., El Camino Real Bridge Realignment Project). Reserve wetlands for future projects by others could also be created as part of the proposed project. The goal is to create a system with a minimum of 50 acres of tidal wetland and approximately 15 acres of brackish wetland. Other areas would be restored as native uplands. Habitat restoration would include excavation of material to lower elevations and open the area to tidal and/or river influence. 1.1 General San Dieguito Lagoon is located within the San Dieguito River Valley in the City of San Diego, San Diego County, California (Figure 1). The San Dieguito Lagoon W-19 Restoration Project (proposed project) would be located within San Dieguito Lagoon, east of lnterstate 5 (I-5), south of County Highway S6, and west of El Camino Real (Figure 2). The proposed project site (W-19) is located within lands owned by the San Dieguito River Park Joint Power Authority (JPA), California Department of Fish and Wildlife (CDFW), 22nd Agricultural District, and the City of San Diego, and is within the Focused Planning Area of the San Dieguito River Park (Figure 3). 1

Figure 1: Regional Map 2

Figure 2: Vicinity Map 3

*The westernmost parcels are currently owned by the City of San Diego, who has an agreement to sell the land to SANDAG once the W-19 site has received all necessary federal and state permits. SANDAG will transfer the property to the JPA after the site meets its success criteria. San Andres Drive Via de La Valle San Dieguito River San Dieguito Rd. Old El Camino Real! " ^ $ Source: JPA: Dokken 2015 I 1,250 625 0 1,250 Feet Scale: 1:15,000 1 inch = 1,250 feet San Dieguito Lagoon W-19 Restoration Project Draft EIR Path: P:\2012\60274999_SD_W19\06GIS\6.3_Layout\Reports\EIR\Ownership.mxd, 2/23/2017, paul.moreno El Camino Real Legend Project Area Disposal Site Temporary Haul Route Ownership City of San Diego SANDAG* San Dieguito River Park Joint Powers Authority (JPA) 22nd District Agricultural Association California Department of Fish and Wildlife SANDAG Technical Services - GIS Figure 3 Ownership Figure 3: Land Ownership Historically, the San Dieguito Lagoon and its adjoining coastal wetlands occupied much of the western San Dieguito River Valley and included a mix of vegetated salt and brackish marsh, with associated tidal 4

embayments, sloughs, and mudflats. The San Dieguito wetlands have experienced extensive filling and alteration, beginning as early as the late 1800s. Between these impacts and simultaneous development of the surrounding area, less than half of the historic wetlands remain intact. Consequently, the ecological function of the tidal marsh ecosystem and the regular influence of the ocean tidal waters have been substantially diminished (SANDAG 2011). Development, infrastructure, and the progressive closing of river and lagoon mouths throughout the San Diego region have led to the conversion and loss of coastal wetlands. The creation of coastal wetlands can offset this historic loss, enhance and maintain sensitive wetland habitats and native species, promote coastal biodiversity within the region, and enrich functional wetland habitat within San Diego. The purpose of the proposed project is to create coastal wetlands, which will be used as mitigation for transportation projects within the coastal corridor of north San Diego County and will partially offset wetland losses within the San Dieguito system. The proposed project would restore habitat that historically occurred within the lagoon, taking into consideration constraints now imposed by existing adjacent land uses and other recently implemented and planned projects. The proposed project would encompass approximately 141 acres, including an area historically identified as a restoration opportunity by the JPA in their 2000 Park Master Plan for the Coastal Area of the San Dieguito River Valley Regional Open Space Park (SDRPJPA 2000). ln addition, the California Department of Transportation (Caltrans) and San Diego Association of Governments (SANDAG) identify the site as part of the overall wetland mitigation strategy for infrastructure projects along the North Coast Corridor within northern San Diego County in the Public Works Plan and Transportation and Resource Enhancement Program (Caltrans 2014). The proposed project is intended to be used for mitigation for infrastructure projects being planned by SANDAG, Caltrans, and/or the City of San Diego (e.g., El Camino Real Bridge Realignment Project). Reserve wetlands and/or uplands for future projects by others could also be created as part of the proposed project. The proposed project would be incorporated into the overall vision of the restored San Dieguito Lagoon system, including other restoration projects as described below, and of the Park Master Plan, which would be updated as part of the proposed project. The Park Master Plan provides a framework for implementing community goals for the restoration of the San Dieguito Lagoon ecosystem, both tidal and nontidal, and for the provision of public access trails and amenities for public enjoyment and nature study (SDRPJPA 2000). The project would restore areas identified in the Park Master Plan (see areas identified as U19, W36, M32, M33, and M37 in the Park Master Plan), as well as other areas west of El Camino Real owned by City of San Diego, CDFW, and 22nd Agricultural District. The existing recreational trail system in the San Dieguito Lagoon ecosystem would also be expanded as part of the project. The Park Master Plan would be amended to redesignate the restored areas as W-19 and incorporate the updated boundaries of restoration and proposed habitat types associated with the proposed project. Other portions of the historic San Dieguito Lagoon system have already undergone restoration efforts, and the proposed project would complement existing restoration efforts. Southern California Edison (SCE) implemented the San Dieguito Wetland Restoration Project, which encompassed approximately 440 acres between El Camino Real and the Pacific Ocean. The SCE project included excavation, restoration of tidal wetlands, reestablishment of historic uplands, and enhancement and expansion of freshwater and seasonal coastal wetland areas, as well as a public access and interpretation component (USFWS and SDRPJPA 2000). The project would be designed to integrate and expand upon SCE's San Dieguito Wetland Restoration Project. The project would also be designed to accommodate ongoing efforts at wetland creation and restoration west of I-5 and south of the Del Mar Fairgrounds, as well as integrate with the 5

proposed El Camino Real Bridge Realignment Project planned by the City of San Diego. The brackish marsh portion of the proposed project is anticipated to provide mitigation for the City's bridge realignment. 1.2. Project Purpose The primary purpose of the proposed project is to restore this coastal area to wetlands, taking into consideration the constraints now imposed by existing adjacent land uses. The project would create both tidal salt marsh and brackish marsh coastal wetlands, which would serve as mitigation for various transportation projects within the coastal corridor of northern San Diego. The project would also enhance connectivity with the broader lagoon ecosystem, promote recreational access within and adjacent to the lagoon and complement existing restoration efforts and flood protection. 1.3. Project Description The proposed project would restore approximately 141 acres to a functional mix of tidal salt marsh, brackish marsh, and transitional/upland habitats. Tidal salt marsh habitat would be created west of the existing utility corridor and brackish marsh habitat east of the utility corridor. Upland/transitional habitats would be placed adjacent to wetland habitat to support ecological function of the restoration project (Figure 4). The existing utility corridor would be enhanced (e.g., through planting with transitional habitat consisting of low-growing, native species that would be maintained by SDG&E) as part of the proposed project. As part of the proposed project, approximately 60 acres of tidal salt marsh would be created west of the existing utility corridor and south of the river. Tidal connection with the San Dieguito River would be constructed at the west end of the project site in the vicinity of the existing least tern nesting island. An upland terrace berm planted with a mix of transitional and upland habitat would be constructed between the salt marsh and the San Dieguito River channel to protect the wetlands from damage due to flood and sedimentation, and to maintain sand movement through the river channel. Figure 4 depicts the approximate boundaries of habitat that would be created by the proposed project. Protection from erosion within the site would be provided along the utility corridor as well as at the outlet of the existing stormwater culvert extending under El Camino Real. East of the existing utility corridor, approximately 15 acres of brackish marsh would be created as part of the proposed project. An open water channel from the San Dieguito River would be constructed through the brackish marsh area. Similar to the salt marsh area, an upland terrace berm planted with coastal sage scrub would be constructed between created brackish marsh habitats and the San Dieguito River channel. The upland terrace berm would be designed to protect the wetlands from damage due to flood and sedimentation, and to maintain sand movement to the ocean. Implementation of the proposed project would require relocation of an existing 69 kilovolt electrical line and poles that extend through the W-19 site. The City of San Diego is planning to underground that segment within existing and planned roadways in the future, but if timing requires relocation prior to that planned implementation, the proposed project would coordinate the relocation to incorporate the line along the existing utility corridor, either within the corridor easement or by increasing the easement up to 20 feet, if necessary. The electrical line would then be redirected along El Camino Real west to reconnect with the system extending south of the W-19 site. In this scenario, the City may underground the electrical line as part of the future project. 6

Figure 4: Proposed Habitat Distribution 7

Habitat restoration activities would include excavation of material to lower elevations and opening of the area to tidal and/or river influence. Excavated material and excess sediment removed during restoration would be transported for disposal either onsite or offsite. There are two potential disposal sites; one site is on City of San Diego land south of the project (onsite, shown in Figure 5) and the other site is Miramar Landfill (offsite). G F! El Camino Real LEGEND Disposal Site* Temporary Haul Route!GF Temporary Construction Entrance Vegetation Coyote Bush Scrub Disturbed/Bare Ground** NOTES: * Limits of Grading same as Disposal Site Boundary **The portion of the disposal site designated as DS-36 continues to be used by SCE. The site was previously mapped as saltbush scrub, but is currently unvegetated. Source: Dokken 2015; AECOM; SANDAG 2014. I 400 200 0 400 Feet Scale: 1:4,800 1 inch = 400 feet Figure 5 Limits of Disturbance Disposal Site San Dieguito Lagoon W-19 Restoration Project Draft EIR Path: P:\2012\60274999_SD_W19\06GIS\6.3_Layout\Reports\EIR\Limits of Disturbance_Disposal Veg.mxd, 3/1/2017, daniel.arellano Figure 5: Limits of Disturbance, Onsite Disposal Option 8

The proposed project would also include construction of a new trail adjacent to El Camino Real (Figure 4). This new trail would extend north from the existing Dust Devil Nature Trail (previously identified as the Mesa Loop Trail in the Park Master Plan) to provide increased recreational opportunities in the lagoon. In addition, a maintenance road extending west from the utility corridor would be constructed within the upland terrace berm to provide access to the salt marsh and existing least tern nesting island. 1.4. Alternatives The proposed project is referred to as Alternative A in the technical studies. Two alternatives to the proposed project are also being evaluated for the salt marsh portion of the site, including an alternative that would allow large flood flows down the San Dieguito River into the created salt marsh area (Alternative B, Figure 6), and an alternative that would create two tidal salt marsh channel systems (Alternative C, Figure 7) separated by an upland terrace berm. Alternatives to the brackish marsh area east of the utility corridor are also being considered, including an alternative that would allow flood flows into the brackish marsh (Alternative B). Project alternatives would still require material disposal at the City disposal sites or Miramar Landfill, but boundaries and acreage of each habitat type created would vary. Each of the alternatives to the proposed project would restore approximately 75-85 acres to a functional mix of tidal salt marsh and brackish marsh. Similar to the proposed project, the alternatives would create tidal salt marsh habitat west of the existing utility corridor and brackish marsh habitat east of the utility corridor. Upland/transitional habitats would also be created adjacent to wetland to provide a gradient of habitat types. 1.4.1. Alternative B Under Alternative B, the habitat distribution would be very similar to that under the proposed project. Approximately 60 acres of tidal salt marsh would be created west of the existing utility corridor, with a western tidal connection to the San Dieguito River south of the existing least tern nesting island. The proposed upland terrace berm area would be planted with a mix of transitional and coastal scrub species, but the elevation of the upland berm would be much lower than that identified for the proposed project. Rather than an ultimate elevation of 20 feet, under Alternative B the upland terrace berm habitat areas would have an elevation of approximately 10 feet and be overtopped during a 25-year or larger storm event. This alternative would therefore be influenced by both tidal exchange and upstream river (fluvial) processes. This differs from the Proposed Project, which would create a system primarily influenced by tidal exchange and would remain protected from fluvial processes (e.g. sedimentation or channel migration) from up to a 100- year flood event. Figure 6 depicts the approximate boundaries of habitat that would be created under Alternative B. Similar to the proposed project, protection from erosion within the site would be provided along the utility corridor, as well as at the outlet of the existing stormwater culvert extending under El Camino Real. Under Alternative B, the existing utility corridor would also be enhanced (e.g., through planting with transitional habitat to be maintained by SDG&E) as described for the proposed project. East of the existing utility corridor, approximately 15 acres of brackish marsh would be created as part of Alternative B. Similar to the proposed project, an open water channel from the San Dieguito River would be constructed through the brackish marsh area. An upland terrace berm would be created between the brackish marsh habitat and the San Dieguito River channel at an elevation of 8 to 11 feet; much lower than 9

that 22 feet elevation upland terrace berm under the proposed project and it is anticipated that this lower berm would be overtopped during a 10-year or greater storm. The existing 69 kilovolt electrical line and poles that extend through the W-19 site would be relocated as part of Alternative B, as described for the proposed project, and habitat restoration activities would include excavation of material to lower elevations and open the area to tidal and/or river influence. Excavated material and excess sediment removed during restoration would be transported for disposal either onsite or offsite, as described for the proposed project. Construction of a new trail adjacent to El Camino Real extending north from the existing Dust Devil Nature Trail (previously identified as the Mesa Loop Trail) to provide increased recreational opportunities in the lagoon would be included as part of Alternative B. ln addition, a maintenance road extending west from the utility corridor along the upland terrace berm would be constructed to provide access to the salt marsh and existing least tern nesting island. 10

Figure 6: Alternative B Habitat Distribution 11

1.4.2. Alternative C Under Alternative C, the habitat distribution would consist of two separate tidal channel systems, one directly adjacent to the San Dieguito River, and one separated from the river by an upland terrace berm. Approximately 70 acres of tidal salt marsh would be created west of the existing utility corridor, with approximately one third of that (22 acres) located adjacent to the river and two thirds (47 acres) protected by the upland terrace berm. The protected portion of the site would have a western tidal connection to the San Dieguito River south of the existing least tern nesting island. The portion of the site adjacent to the river would connect to the river east of the nesting site, but would be anticipated to evolve from wetlands to transitional and upland over time as storm flows from the river deposit river sediment on the site. The proposed upland terrace area would be planted with a mix of transitional and coastal scrub species, and would be at an elevation of 22 feet, similar to that identified for the proposed project. Alternative C would provide systems representative of both the Proposed Project and Alternative B; the area protected by the upland terrace berm would be primarily tidally influenced, similar to the Proposed Project, while the area adjacent to the river would be initially influenced both by tidal and fluvial processes, but after major storms of 25-yr or greater frequency the unprotected wetlands area would be filled with river sediment (similar to Alternative B). Figure 7 depicts the approximate boundaries of habitat that would be created under Alternative C. Similar to the proposed project, protection from erosion within the site would be provided along the utility corridor, as well as at the outlet of the existing stormwater culvert extending under El Camino Real. Under Alternative C, the existing utility corridor would also be enhanced (e.g., through planting with transitional habitat to be maintained by SDG&E) as described for the proposed project. East of the existing utility corridor, the brackish portion of the site would be created as discussed under the proposed project. Approximately 15 acres of brackish marsh would be created as part of Alternative C, with an open water channel through the site. Similar to the salt marsh area, an upland terrace berm planted with coastal sage scrub would be constructed at an elevation of approximately 22 feet between created brackish marsh habitats and the San Dieguito River channel. The upland terrace berm would protect the wetlands from damage due to flood and sedimentation, and maintain sand movement to the ocean. The existing 69 kilovolt electrical line and poles that extend through the W-19 site would be relocated as part of Alternative C, as described for the proposed project, and habitat restoration activities would include excavation of material to lower elevations and open the area to tidal and/or river influence. Excavated material and excess sediment removed during restoration would be transported for disposal either onsite or offsite, as described for the proposed project. Construction of a new trail adjacent to El Camino Real extending north from the existing Dust Devil Nature Trail (previously identified as the Mesa Loop Trail) to provide increased recreational opportunities in the lagoon would be included as part of Alternative C. ln addition, a maintenance road extending west from the utility corridor along the upland terrace berm would be constructed to provide access to salt marsh and the existing least tern nesting island. 12

Figure 7: Alternative C Habitat Distribution 13

1.4.3. No Project Alternative Under the No Project Alternative, no restoration of the W-19 site would occur by SANDAG and additional wetlands would not be created on the site to complement adjacent restoration projects. Regional coastal wetlands would not be increased and the identification of alternative mitigation areas for the North Coast Corridor and El Camino Real Realignment Project would be required. The Park Master Plan would not be expanded, and benefits associated with increased tidal system and public access would not be realized, although future restoration of the site would not be precluded. The JPA could pursue restoration in the future through alternative partnerships or approached, although no alternative funding for such restoration has been identified at this time. Under the No Project Alternative, it is assumed vegetation on the site would continue to be dominated by disturbed scrub and non-native grasslands, and invasive species within existing riparian areas would continue to encroach along the river. It is assumed that SDG&E would continue to maintain vegetation along the existing utility corridor to facilitate operations and maintenance of the various utilities traversing the site. Since no excavation of material would occur under the No Project Alternative, no material would require disposal onsite or offsite, and while a trail connection would not be constructed along El Camino Real between the Dust Devil and Coast to Crest trails, the addition of trails in the site would not be precluded. The JPA could pursue individual trail projects independently in the project area in the future. Similarly, relocation of the electrical line traversing the W19 site would not be required if the proposed project is not implemented. The City of San Diego has plans identifying relocation of the electrical line as part of an undergrounding program that would move the line into existing and proposed street segments, although specific timing for implementation of that program has not been set. Either the City or SDG&E could therefore pursue relocation in the future if desirable. This W-19 project may result in sediment deposition at the connection point between this site and the San Dieguito River channel, as well as at other locations. Various stormflow scenarios were evaluated by the U.S. Army Corps of Engineers (USACE) for their sediment delivery using the AdH numerical model. A complete description of this work is presented in USACE (2015). The AdH model shows that maintenance dredging of the sediment at the mouth of W-19, and at other locations, will be required to maintain the connection between the new wetland, the existing wetland, and the River. The frequency and magnitude of this dredging is analyzed herein for the various alternatives. 1.5 Existing and Recently Restored Wetlands Between 2006 and 2012 Southern California Edison (SCE) increased the San Dieguito Lagoon by approximately 150 acres as mitigation for the San Onofre Nuclear Generating Station (SONGS) project. This restoration project increased the tidal prism of the lagoon, added new marshes and subtidal areas, and shifted the ocean entrance channel slightly to the north from its prerestoration position. As before, sand from the marine environment (littoral sand) is deposited in the vicinity of the ocean entrance channel over time as it is drawn into the lagoon by tidal currents and pushed into the channel by waves. This sand requires periodic maintenance dredging to preserve the hydraulic connectivity of the lagoon mouth. As part of the mitigation for SONGS, SCE 14

is responsible for maintaining an open lagoon mouth. The full description of the maintenance dredging anticipated at the ocean entrance channel for the SCE project is found in the Update of Restored San Dieguito Lagoon Inlet Channel Excavation and Dredging Plan (Coastal Environments 2010). The SCE lagoon restoration occurred in multiple phases with the internal lagoon area being restored first in 2008-2010, and the tidal entrance channel being restored second in 2011 and 2012. The SCE San Dieguito Lagoon Restoration Project plan is shown in Figure 8. Figure 9 shows the tidal inlet channel construction dredge plans. The future maintenance dredging area is shown in Figure 10, and a typical section is shown in Figure 11. Maintenance dredging of the ocean inlet would serve to restore this channel configuration. The SCE maintenance dredging is designed to create a channel that is slightly deeper than an equilibrium condition to collect sand between Camino Del Mar and the Railroad Bridge as a sand management area to facilitate future maintenance dredging. Three different areas will be considered for maintenance needs for the W-19 project. The primary maintenance dredging location is the existing tidal entrance channel near the beach. SCE already intends to maintain the channel by dredging. This memo will address the impact of the W-19 project on the magnitude and frequency of the inlet dredging. The second important maintenance dredging location to consider is the new W-19 wetland inlet channel, and the third site that may potentially need to be dredged and be impacted by W-19 is the entrance channel to site W-4. This memo does not address maintenance dredging of W-4 because the AdH model results show that the W-19 project does not increase the dredging requirement at W-4. 15

Figure 8: San Dieguito Lagoon Project Restoration Plan (Source: Coastal Environments 2010) 16

Figure 9: San Dieguito Lagoon Tidal Inlet Construction Dredging Plan (Source: Coastal Environments 2010) 17

Figure 10: San Dieguito Lagoon Project Restoration Tidal Inlet Maintenance Dredge Plan (Source: www.sdrp.org) Figure 11: San Dieguito Lagoon Project Restoration Tidal Inlet Maintenance Dredge Typical Section (Source: www.sdrp.org) 18

2. MAINTENANCE DREDGING REQUIREMENTS 2.1 Ocean Inlet Channel to the San Dieguito River The ocean inlet channel to the San Dieguito River will require maintenance dredging on an biennial basis per the SCE design project. Thus far maintenance dredging has only occurred once (in Fall of 2015) since construction the project in 2011. The quantity that was dredged for maintenance was 16,000 cubic yards (cy) and the placement location was at Del Mar beach just south of the tidal inlet channel. Future placement may occur either south or north of the channel, depending on the direction of longshore sand transport at the time. Sand deposition during a northward longshore drift condition would trigger placement north of the lagoon mouth, and vice-versa. Figure 12 shows the proposed beach placement area for the sand; S1, the location north of the channel and S3, the location south of the channel. SCE maintenance dredging utilizes earthmoving equipment to dig sand from the channels and off-road trucks to transport it to the beach. The Excavation and Dredging Plan (Coastal Environments 2010) discusses use of 2 excavators, 5 scrapers and a front end loader to do the work. Sand is to be removed from up to 4 different areas, as shown in Figure 13. Area 1 is from the ocean to Camino Del Mar; area 2 is from Camino Del Mar to the Railroad Bridge; area 3 is from the Railroad Bridge to Jimmy Durante Bridge, and area 4 is upstream of Jimmy Durante Bridge. The coastal engineer for SCE (Hany Elwany Ph.D., Coastal Environments, Personal Communication) was contacted to update the status of the maintenance dredging at the site. Dr. Elwany indicated that maintenance dredging had only occurred once since construction for two reasons. The first reason is that the tidal entrance channel performed well and there was no need to dredge before 2015. Second, the Railroad Bridge has become the focus of concern of multiple parties and a decision was made to postpone maintenance dredging in its vicinity until it could be confirmed that dredging would not adversely affect the bridge. Of the 16,000 cy dredged from the channel, 2,000 cy was dredged from area 1 and 14,000 cy was dredged from area 2. The work required 2 to 3 weeks to complete. 19

Figure 12: Sand Placement Areas for San Dieguito Lagoon Maintenance Dredging (Pink Polygons) Source: Coastal Environments 2010 20

Figure 13: Maintenance Dredging Areas for San Dieguito Lagoon 21

Impacts of the W-19 project on dredging of the San Dieguito Lagoon tidal entrance channel are predicted to be relatively small. As presented in Moffatt & Nichol, or M&N, (2015), the tidal prism of San Dieguito Lagoon would increase approximately 30% with any of the W19 wetlands restoration alternatives, and the tidal flow velocity through the ocean tidal inlet would increase approximately 10%. Increasing the tidal prism and tidal velocity will increase the flushing of sediment from the ocean inlet; however, it would also bring more sediment into the system, thus increasing the ultimate maintenance dredging quantities, and potentially the maintenance area. The tidal ebb velocity through the tidal inlet is estimated to be less than 3 feet per second (fps) under the shoaled condition after restoration, and approximately 3 fps under the post-restoration dredged condition. This velocity is not high enough to maintain a stable inlet without maintenance dredging, therefore maintenance dredging will continue to be necessary, as indicated by Coastal Environments (2010). A conservative estimate is that the preferred W-19 restoration project (Alternative A) may increase the biennial maintenance sediment removal requirement by approximately 4,200 cy, approximately 25% more than the original SCE quantity. The volume for removal is based on analyzes presented in the the memo titled Sand Loss Estimation and Mitigation, San Dieguito Lagoon W-19 Project by M&N (2016). The memo identifies an annual sand quantity increase in littoral sand deposition at the mouth of 2,100 cy. The impact to SCE biennial dredging is double this volume to 4,200 cy every other year for maintenance sediment removal. To address this increase in littoral sand deposition resulting from W-19, SANDAG will either increase the capacity of the inlet as part of the project or pay SCE to increase the inlet capacity at the time of their inlet maintenance. This additional littoral sand, if not captured in the sand trap below the railroad bridge would effectively be lost from the coastal sediment budget. The existing sand trap will be enlarged by either deepening a portion of the existing sand trap or increasing the size of the sand trap to accommodate an additional 4,200 cy. The existing sand trap will be enlarged between Camino Del Mar and the Railroad within Area 2 of the designated dredge area for SCE. The existing sand volume available for maintenance dredging within the SCE permitted areas between the Camino Del Mar and Railroad Bridges is nearly 32,000 cy, as determined by estimating the surface area of maintenance sub areas within Area 2 and multiplying them by their target depths to obtain approximate volumes, and summing the totals. This quantity is sufficient to provide the needed maintenance for both projects. Also, the beach placement sites possess sufficient capacity to receive all of this material. The beach receiver site footprints are capable of receiving approximately 50,000 cy of sand total. This volume was determined by estimating the length of the beach receiver sites, and estimating a beachfill profile, and multiplying the new profile by the beach length to obtain sand volume. 2.2 W-19 Brackish and Salt Marsh Entrances and Interior Areas The criteria for maintaining the brackish and salt marsh areas are the following: Sediment is blocking tidal flows to wetlands Sediment is creating stagnant or isolated areas that could create a health hazard (mosquitos) The depth of sediment is 6 or more in wetlands designated for adaptive management and replanting on top of the sediment would not support the original habitat type. 22

These two marshes are discussed as a unit below with regards to volumes, and then subdivided into separate geographic areas for more detailed discussion of sediment removal procedures. The numerical modeling results show sedimentation for 10 year, 25 year, 50 year, 100 year storms, and in series over 100-years (the 100-year series). Analyzing results against maintenance criteria indicate that sediment removal actions would occur after a 25-year storm or greater (i.e. 50-year and 100-year storms). Model results showing sedimentation for the three specific stormflow scenarios (25-, 50-, and 100-year storms) under Alternative A (the proposed project) are shown in Figures 14 through 16. Figure 14: Sedimentation From the 25-Year Storm for the San Dieguito River for Alternative A 23

Figure 15: Sedimentation From the 50-Year Storm for the San Dieguito River for Alternative A Figure 16: Sedimentation From the 100-Year Storm for the San Dieguito River for Alternative A 24

Sediment removal opportunities from marshes for the various alternatives under these storm events are listed below and shown in Figures 17, 18 and 19 for the alternatives: Proposed Project (Alternative A) Brackish and salt marsh entrances after storm events of 25- years or greater; adaptive management for interior areas shown in Figure 17 where sedimentation depths exceed 6 inches after 50-yr and 100-yr events; Alternative B Brackish and salt marsh entrances after storm events of 25 years or greater; no maintenance proposed for interior areas where modeling shows large volumes of sediment based on resource agency input to allow the wetland/upland habitat distribution to evolve over time based on river dynamics; and Alternative C - Brackish and salt marsh entrances after storm events of 25-years or greater; adaptive management for interior protected areas shown in Figure 19 where sedimentation depths exceed 6 inches after 50-yr and 100-yr events; maintenance within the portion of the wetland adjacent to the river would not occur under this alternative in order to allow the site to evolve based on river dynamics. Deposition within the interior of the restored brackish marsh is also predicted as a result of severe storm events. Sediment deposition in these areas is difficult to predict; therefore, maintenance frequency and volumes within interior portions of W-19 are very speculative. Maintenance of interior portions of the salt marsh and/or brackish marsh is not specifically anticipated. After severe storm events that result in deposition in the interior of the wetlands, an analysis to identify deposition areas and depths, as well as potential impacts to habitat resulting from deposition or maintenance, would be conducted. Based on this analysis, it is anticipated that adaptive management strategies would be implemented to maintain the function of the restored W-19 wetland areas shown in Figures 17 and 19. The volumes of sediment estimated to be removed from the brackish marsh and salt marsh entrances for each alternative during specific storm events and the 100-year series are shown in Table 1 below. These volume estimates assume a 25% reduction in the model calculated sediment volumes to account for uncertainties in the modeling, equipment access and methods of sand removal. 25

Table 1: Sediment Maintenance Volumes from Marsh Entrances for Alternatives Under Each Modeling Scenario (1,000 cy) Event Project Alternative B Alternative C 10-yr N.A. N.A. N.A. 25-yr 5 2 6 50-yr 20 15 20 100-yr 15 20 10 100-yr Series 20 15 15 Approaches to sediment removal for each maintenance subarea of the marshes are described below. 26

Figure 17: Sediment Removal Areas For Alternative A 27

Figure 18: Sediment Removal Areas For Alternative B 28

Figure 19: Sediment Removal Areas For Alternative C 29

2.2.1 Salt Marsh The salt marsh collects sediment in two different places, depending on the magnitude of the storm flow event, and the alternative. For the proposed project and each alternative, the entrance of the salt marsh collects sediment during the major storm flow events analyzed using the model. The east end of the salt marsh also receives sediment that overflows the utility corridor during very large storm events. Maintenance at the east end of the salt marsh is anticipated as an adaptive management action for the proposed project (Alternative A) and Alternative C. Maintenance of the inlet and east end areas are discussed below. All Alternatives - Tidal Entrance Channel to W-19 Maintenance dredging of the tidal entrance channel to the W-19 salt marsh would only be needed on a periodic, as-needed basis. Modeling suggests significant sediment accumulation at the inlet after a 25- year storm or larger (USACE 2015) resulting in a sand bar across the mouth-blocking tidal flows. Based on the modeling, no maintenance will be anticipated for storms smaller than the 25-year event because the sediment deposition layer would be too thin to affect the habitat and to justify the expense of removal and placement on the beach. Removal of the bar could be done using land-based equipment consisting of an excavator and/or backhoe that loads 10-cy capacity trucks (rear dumps). The access point(s) would be the levee north of the W-19 mouth, or the high ground south of the mouth. A temporary access road from the north could be installed along the levee bank from the levee crest down to the sand bar excavation area, or from the south along the river bank from high ground to the sand bar. The likely scenario would involve the excavator crawling down the levee or river bank to the sand bar, and moving on top of the sand bar to position itself at the far end of the sand bar from the access point. Trucks would then drive onto the sand bar to the excavator, receive a load, and turn around and drive out of the site. The excavator would gradually work its way backward toward the truck access point, removing sand as it goes. Eventually, the excavator would back up to the levee while removing sand, and the work would be complete. The sand bar is assumed to be able to support the weight of the equipment, and appears in the modeling graphics to be wide enough to enable a turn around. This approach is very similar to that which occurs annually at the mouth of San Elijo Lagoon. Figure 20 shows a concept of the truck access route. 30

Figure 20: Truck Access and Excavation Area for the Mouth of W-19 Alternatives A and C - East End of Saltwater Marsh Maintenance dredging of the east end of the saltwater marsh would only occur for Alternatives A and C when adaptive management concludes that sufficient material volume has been deposited near the utility corridor to warrant removal. Without consideration of sea level rise, modeling shows a area of deposition greater than 6 at the east end after the 50-year and 100-year storm for the project and after the 100-yr storm for Alternative C. Sediment is predicted to be deposited just west of the utility corridor, as shown in Figure 17 for the project and Figure 19 for Alternative C. Removal of sediment could be done using land-based equipment consisting of a long-reach excavator and/or long-arm backhoe that loads 10-cy capacity trucks (rear dumps). The probable scenario would involve constructing a short temporary access road from the utility corridor on the deposited material for removal of sediment for Alternatives A and C, and possibly queuing the trucks on the utility corridor. Trucks should be able to drive onto the utility corridor and turn around for greater ease of movement. El Camino Real provides access to the site from the local road network. 2.2.2 Brackish Marsh - Entrance Channel and Overbank Areas Maintenance dredging of the entrance channel to the brackish marsh is required for all alternatives on a periodic, as-needed basis. The internal overbank area for Alternatives A and C would also potentially need 31

dredging as an adaptive management action. Modeling suggests significant sediment accumulation at the marsh entrance after a 25-year storm or larger (USACE 2015) resulting in a sand bar along the inside south west bank of the utility corridor. Figure 21 shows an example of potential access to the sand bar by construction equipment. Removal of sediment from the entrance or internal brackish marsh could be done using land-based equipment consisting of a long-reach excavator and/or long-arm backhoe that loads 10-cy capacity trucks (rear dumps). The access point(s) would be the berm north of the brackish marsh and/or the utility corridor. Trucks may have to back in to the levee, while they may be able to drive onto the utility corridor and turn around for greater ease of movement. El Camino Real provides access to the sites from the local road network. Figure 21: Truck and Excavator Access and Excavation Areas for the Brackish Marsh 2.2.3 Sand Transport Routes and Beach Placement Sites Sediment removed in maintenance is assumed to be beach quality sand and able to be placed at the beach at historic placement sites. Trucks would haul the material from the W-19 site east to El Camino Real and follow the following route to the beach: 32

1. El Camino Real north to Via De La Valle; 2. Via De La Valle west to Camino Del Mar; 3. Camino Del Mar south to: a. a turn-out north of the River for dirt road access to dog beach, and/or b. residential street ends at 20 th Street and 18 th Street to the beach. Figure 22 shows the potential route for sand hauling. This work would require approximately 10 work days for the post-25 year storm event, assuming an equipment production rate of 500 cy per day. The duration increases four-fold for the 50-year event, and three-fold for the 100-year event. Table 2 shows the duration of work for each alternative for specified storm events. Figure 22: Truck Haul Route Anticipated maintenance volumes, as well as required truck trips (in round trips) and estimated durations for maintenance activities after storms of varying intensities, is provided in Tables 2-4 on the following page. 33

Table 2 - Project Storm Frequency Maintenance Area Maintenance Volume (cy) 1 Truck Round Trips (8cy/trip) Duration (working days) 2 25-year Total 5,000 625 13 Salt Marsh Inlet 1,000 Brackish Marsh Inlet 4,000 50-year Total 20,000 2,500 43 Salt Marsh Inlet 1,000 Brackish Marsh Inlet 19,000 100-year Total 15,000 1,875 33 Salt Marsh Inlet 1,000 Brackish Marsh Inlet 14,000 Table 3 Alternative B Storm Frequency Maintenance Area Maintenance Volume (cy) 1 Truck Round Trips (8cy/trip) Duration (working days) 2 25-year Total 2,000 250 7 Salt Marsh Inlet 1,000 Brackish Marsh Inlet 1,000 50-year Total 15,000 1875 33 Salt Marsh Inlet 1,000 Brackish Marsh Inlet 14,000 100-year Total 20,000 2,500 43 Salt Marsh Inlet 1,000 Brackish Marsh Inlet 19,000 34

Table 4 Alternative C Storm Frequency Maintenance Area Maintenance Volume (cy) 1 Truck Round Trips (8cy/trip) Duration (working days) 2 25-year Total 6,000 750 15 days Salt Marsh Inlet 1,000 Brackish Marsh Inlet 5,000 50-year Total 20,000 2,500 43 days Salt Marsh Inlet 2,000 Brackish Marsh Inlet 18,000 100-year Total 10,000 1,250 23 days Salt Marsh Inlet 2,000 Brackish Marsh Inlet 8,000 1. Maintenance volumes assume 25% of deposited material would remain in place and would not be removed. 2. Activities on the beach would be 2 days less than overall maintenance activities, rates for removal/transport are assumed to be 500 cy/day, working 10 hours/day. Mobilization and demobilization and construction of temporary access roads would require an additional 3 days. Verification of the sand quality would be needed through a Sampling and Analysis Plan process consistent with the Inland Testing Manual prepared by the U.S. Environmental Protection Agency (USEPA) and U.S. Army Corps of Engineers (USACE) in 1998 called the Green Book. Sand analysis through this process requires sampling and testing for grain size and chemistry. Typically, characterization of the sand grain size at the receiving beach needs to be developed for comparison with the River sand to determine its compatibility for beach placement. Permits from the USACE, Regional Water Quality Control Board, California Coastal Commission, City of Del Mar, and possibly the California Department of Fish and Wildlife would have to be secured for beach placement of the sand. 3. CONCLUSIONS Conclusions are provided below for sedimentation at both marshes and for shoaling at the tidal entrance channel near the ocean. 3.1 Ocean Entrance Channel Effects of restoring the W-19 site may necessitate additional dredging of the ocean entrance near the ocean. SCE is presently responsible for that maintenance. The W-19 project may draw additional sand upstream through the tidal entrance due to increased tidal prism of the River. A separate memo (M&N 2016) indicates that the W-19 project could potentially reduce sediment supplies to the ocean by 2,100 cy per year. That same sand quantity can represent the added maintenance requirement and could be removed from the tidal entrance channel on a regular basis and returned to the beach. The SCE 35

maintenance dredging requirement would be increased by 4,200 cy every other year, or approximately 25%, by this action. To mitigate for the loss of sand from the coastal sediment budget due to increased entrainment of material in the San Dieguito River inlet, the W-19 project will enlarge the sand trap created and maintained by SCE in the river channel bottom. The larger sand trap will capture the additional sand entrained in the river mouth as a result of the proposed project. The existing and larger sand trap will be a depression in the river bottom, capturing sandy material before it can travel up the river channel to a location beyond the reach of feasible sand removal. 3.2 Sedimentation at the W-19 Salt and Brackish Marshes Sedimentation removal at the brackish and salt marshes is summarized below. For both sites, if the sediment is determined suitable for beach placement through a Sampling and Analysis Plan process, the sand could be hauled by truck through San Diego and Del Mar surface streets to the beach. Two beach placement sites may be available in Del Mar, with one at dog beach to the north of the River, and the other at the foot of 18 th and 20 th Streets. Permits would have to be secured for both excavation and beach placement of the sand. 3.2.1 Salt Marsh Sand deposited near the mouth of the W-19 restoration site after major storm events will need to be removed to maintain adequate tidal flushing in the wetlands. Sand quantities for removal from W-19 vary depending on the magnitude of the storm event. The east end of W-19 salt marsh may also need sediment removal as adaptive management for the project (Alternative A) after the 50-year and 100-year stormflow and after the 100-year stormflow for Alternative C. This work can be accomplished by conventional earthmoving equipment in relatively dry conditions. The proposed levee along the northern perimeter of W-19 can provide access to the downstream salt marsh excavation area, while the utility corridor can provide access to the eastern salt marsh area. 3.2.2 Brackish Marsh Sand deposited near the mouth of the brackish marsh after major storm events will need to be removed to maintain adequate flow to and from the wetlands. The wetland entrance near the utility corridor is the primary removal site, with potential sediment removal from the internal overbank area as an adaptive management action. Sand quantities for removal from the site vary depending on the magnitude of the storm event. This work can be accomplished by conventional earthmoving equipment in relatively dry conditions. The utility corridor can also provide access to the entrance channel and the interior area. Approximately 7 to 15 working days are required to perform all of this work combined (salt and brackish marshes) for the 25-year storm event, and durations tend to increase for larger-magnitude storm flow events. 36

3.1.1 Riverine Sediment Deficit and Mitigation The fluvial hydraulic modeling performed by the U.S. Army Corps of Engineers (ACE) predicts a 75,000 cy reduction in sediment volume reaching the Jimmy Durante Blvd bridge as the result of the W-19 project. This reduction was derived by the model based on applying a series of assumed storm events over a period of 100-years. This series of storm events or 100-yr storm series was taken from the Southern California Edison hydraulic analysis performed by Dr. Howard Chang (Chang 2004). This reduction in sediment does not occur uniformly over the 100 years, but episodically based on the magnitude of the storm event. Below table 5 shows the sediment deficit for the project and each alternative for a variety of storm periods. Table 5 - Sediment Delivery/Deficit to Ocean (1000s cubic yards) Event Existing Project Delivery Project Deficit Alt B Delivery Alt B Deficit Alt C Delivery Alt C Deficit 10-yr 25 23 2 20 5 22 3 25-yr 142 127 15 101 41 122 20 50-yr 321 312 9 258 63 298 23 100-yr 407 433 (26)* 370 37 420 (13)* 100-yr Series 990 915 75 734 256 889 101 *surplus Table 6 shows the expected volume of sediment that will be removed from the W-19 inlets during maintenance after major storm events for the project and Alternatives, and the trucking required to complete the work. Over the course of the 100-year storm series used for modeling purposes, inlet maintenance is anticipated to return approximately 20,000 cy to the beach for the project, as shown in Table 1 and adaptive management maintenance is anticipated to return an additional 25,000 cy to the beach, as shown in Table 6. Therefore, the long-term net loss from fluvial delivery for the project would total approximately 30,000 cy (75,000 cy deficit minus 20,000 cy returned from inlet maintenance minus 25,000 cy returned from adaptive management maintenance). 37